CN111747623A - Integrated treatment process for oily sludge - Google Patents

Integrated treatment process for oily sludge Download PDF

Info

Publication number
CN111747623A
CN111747623A CN202010564569.6A CN202010564569A CN111747623A CN 111747623 A CN111747623 A CN 111747623A CN 202010564569 A CN202010564569 A CN 202010564569A CN 111747623 A CN111747623 A CN 111747623A
Authority
CN
China
Prior art keywords
sludge
water
thawing
freezing
oil
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010564569.6A
Other languages
Chinese (zh)
Inventor
王晓东
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Xinjiang Boyun Times Environmental Protection Technology Co ltd
Original Assignee
Xinjiang Boyun Times Environmental Protection Technology Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Xinjiang Boyun Times Environmental Protection Technology Co ltd filed Critical Xinjiang Boyun Times Environmental Protection Technology Co ltd
Priority to CN202010564569.6A priority Critical patent/CN111747623A/en
Publication of CN111747623A publication Critical patent/CN111747623A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/305Treatment of water, waste water, or sewage by irradiation with electrons
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/002Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal in combination with oil conversion- or refining processes
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/46Recuperation of heat
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/001Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Toxicology (AREA)
  • Health & Medical Sciences (AREA)
  • Wood Science & Technology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention belongs to the technical field of oily sludge treatment, and particularly relates to an integrated treatment process of oily sludge, which comprises the following steps: s1, crushing and homogenizing the oily sludge, and then adding water to control the water content of the sludge to form sludge to be frozen and thawed; s2, repeatedly freezing and thawing the sludge to be frozen and thawed, wherein three-phase separation is realized by layering of each freezing and thawing, the layered sludge enters next freezing and thawing, and a sludge melting layer, a water melting layer and an oil phase are obtained after the repeated freezing and thawing is completed; and S3, treating the molten mud in an incineration system, treating the molten water layer in a water treatment system, and treating the oil phase in an oil purification system. The oily sludge integrated treatment process adopts crushing homogenization and freeze thawing methods to realize the complete separation of water, sludge and oil, and oil enters a product purification system, a water inlet treatment system and a sludge inlet incineration system.

Description

Integrated treatment process for oily sludge
Technical Field
The invention belongs to the technical field of oily sludge treatment, and particularly relates to an integrated treatment process of oily sludge.
Background
In the upstream exploration and development, oil and gas gathering and transportation, sewage treatment, tank bottom cleaning and downstream petroleum smelting processes of petroleum, a large amount of mixed leakage containing petroleum hydrocarbons is generated to the environment due to process equipment, manual operation and the like, and the solid and semisolid mixed leakage is called as oily sludge.
The oily sludge has complex components, generally consists of oil-in-water, water-in-oil and suspended solids, and is a stable suspended emulsion semi-liquid system. The sludge particles are fine and are flocculent inside. The water-oil emulsified oil has small density difference between oil and water, high water content of 40-90%, sufficient emulsification, high viscosity and difficult sedimentation. The sludge particles have poor stability, are easy to decay and generate stink, pollute air and have great harmfulness in production and environmental protection. The oily sludge has complex components and greatly different physical and chemical properties, so the treatment technology is also diversified.
At present, the treatment methods for treating the oily sludge mainly comprise incineration, thermal desorption, thermal cracking, solvent extraction and the like. The pure incineration and thermal desorption involve high temperature, so that high energy consumption is inevitable, and the waste of crude oil resources is also caused. The extraction separation is a simple and efficient final treatment technology for recycling oil sludge resources, the separation process is relatively short in time consumption, but the extraction separation needs a large amount of solvents, the treatment cost is high, and the environmental impact is large. Moreover, due to the diversity and complexity of the varieties of the oil sludge, different organic solvents need to be developed for extraction.
Most of the existing methods for treating the oily sludge are direct incineration or thermal desorption after oil separation, wherein the oil separation methods mainly comprise hot washing, medicament cleaning, mechanical conditioning and demulsification and the like, and comprise the following steps: the patent document with publication number CN 108996859a discloses a green cleaning-thermal desorption integrated technology treatment method for high-concentration petroleum sludge, which comprises the treatment steps of homogeneous impurity removal pretreatment, chemical thermal cleaning treatment, solid-liquid separation and oil-water separation, thermal desorption of oil sludge, high-temperature combustion oxidation, heat exchange and tail gas cooling and dust removal; the process mainly realizes the deep purification of the oil sludge through impurity removal, thermal washing, solid-liquid separation and thermal desorption, the wastewater generated by washing the oil sludge in the process is treated by a wastewater integrated device and then recycled, and in addition, the heat in the thermal desorption process can be used as a heat source for thermal washing and drying to realize the recycling of thermal resources. However, the existing treatment method of the oily sludge still has the problems of incomplete three-phase separation of oil sludge and water or low oil recovery efficiency, and causes a certain waste of energy. In addition, a large amount of secondary pollution such as waste water, waste gas and the like is generated in the treatment process.
Disclosure of Invention
Based on the defects in the prior art, the invention provides an integrated treatment process for oily sludge.
In order to achieve the purpose, the invention adopts the following technical scheme:
an integrated treatment process of oily sludge, comprising the following steps:
s1, crushing and homogenizing the oily sludge, and then adding water to control the water content of the sludge to form sludge to be frozen and thawed;
s2, repeatedly freezing and thawing the sludge to be frozen and thawed, wherein three-phase separation is realized by layering of each freezing and thawing, the layered sludge enters next freezing and thawing, and a sludge melting layer, a water melting layer and an oil phase are obtained after the repeated freezing and thawing is completed;
and S3, treating the molten mud in an incineration system, treating the molten water layer in a water treatment system, and treating the oil phase in an oil purification system.
Preferably, in the step S1, the water content of the sludge is controlled to be 60 to 80%.
Preferably, the water content of the sludge is controlled to be 68-72%.
Preferably, the repeated freezing and thawing comprises secondary freezing and thawing, and the melted mud after the primary freezing and thawing is mixed with water for secondary freezing and thawing.
Preferably, the freeze-thaw process conditions include: the freezing temperature is-25 to-5 ℃, and the freezing-thawing time is 4 to 15 hours.
Preferably, the freeze-thaw process conditions include: the freezing temperature is-20 to-15 ℃, and the freezing-thawing time is 8 to 10 hours.
As a preferred scheme, the water-melting layer is treated by flocculation and electron beam irradiation in a water treatment system, the treated water is discharged after reaching the standard or recycled to be used as water supply for freeze thawing treatment, and the solid obtained by flocculation enters an incineration system for treatment.
Preferably, the process parameters of the electron beam irradiation include: the energy is 1.2-2.5 MeV, the current is 1-10 mA, and the irradiation time is 60-120 s.
As a preferred scheme, the oil phase enters an oil product purification system for treatment to obtain purified oil, and the combustion heat value of the purified oil can reach 37560-39785 kJ/kg.
Preferably, the purified oil is used for supplying energy to an incineration system, and the waste heat of the incineration system is used for defrosting and preheating the frozen and melted mud and melted water layer.
Compared with the prior art, the invention has the beneficial effects that:
the oily sludge integrated treatment process adopts crushing homogenization and freeze thawing methods to realize three-phase separation of water, sludge and oil, wherein the oil enters a product purification system, a water inlet treatment system and a sludge inlet incineration system; through oil purification, the recovered oil is close to the quality of crude oil, and part of the recovered oil can be used as heat supply for sludge incineration; performing advanced treatment on the water-melting layer subjected to freeze thawing and demulsification through flocculation and electron beam irradiation technologies, and discharging the water-melting layer up to the standard or recycling the water-melting layer to freeze thawing treatment; the fused mud enters an incineration system, and the waste heat of the incinerated tailings and tail gas can be used as heat sources for unfreezing and preheating the fused mud and the fused water layer.
The oily sludge integrated treatment process realizes the cyclic utilization of resources.
Drawings
FIG. 1 is a flow chart of the integrated treatment process of oily sludge in example 1 of the present invention.
Detailed Description
In order to more clearly illustrate the embodiments of the present invention, the following description will explain the embodiments of the present invention with reference to the accompanying drawings. It is obvious that the drawings in the following description are only examples of the invention, and that for a person skilled in the art, other drawings and embodiments can be derived from them without inventive effort.
The integrated treatment process of the oily sludge provided by the invention can realize multiple effects of recycling, reducing, harmlessness and the like of the oily sludge, and can realize the recycling of resources such as petroleum substances, heat and the like. The purpose of demulsification is achieved by adopting a freeze thawing method and utilizing the difference of oil-water freezing points, and compared with the conventional hot washing and demulsification, the demulsification method avoids adding excessive agents and does not introduce other pollutants.
Example 1:
as shown in fig. 1, the integrated treatment process of oily sludge of the present embodiment includes the following steps:
s1, pretreating the oily sludge, and specifically comprises the following steps: crushing and homogenizing the oily sludge, and then adding water to control the water content of the sludge to form sludge to be frozen and thawed;
specifically, the water content of the sludge is controlled to be 60-80%.
More preferably, the water content of the sludge is controlled to be 68-72%; when the water content is higher, the volume of water drops is larger, the supercooling effect is reduced, the freezing point is not greatly reduced, and the freezing effect is more obvious; if the water content is too much, the waste of resource and energy consumption is caused.
S2, repeatedly freezing and thawing the sludge to be frozen and thawed in a freezing and thawing system, realizing three-phase separation by layering of each freezing and thawing, performing next freezing and thawing on layered sludge, and obtaining sludge, a water-melting layer and an oil phase after the repeated freezing and thawing is completed;
particularly, the freeze thawing method is more convenient in extremely cold areas and can save energy supply;
the freeze-thaw process conditions of the present example include: the freezing temperature is-25 to-5 ℃, and the freezing and thawing time is 4 to 15 hours;
more preferably, the freezing temperature is-20 to-15 ℃, and the freezing-thawing time is 8 to 10 hours.
The repeated freezing and thawing of the embodiment comprises secondary freezing and thawing, and the melted mud after the primary freezing and thawing is mixed with water for secondary freezing and thawing, so that the oil content of the melted mud is further reduced.
And S3, treating the molten mud in an incineration system, treating the molten water layer in a water treatment system, and treating the oil phase in an oil purification system.
Specifically, the molten sludge of the embodiment is thawed and homogenized, passes through the pre-dry heating system, and enters the incineration system for incineration treatment. The heat exchange heat source of the incinerated tailings and the incinerated tail gas can be used for thawing and preheating the melted mud and the melted water layer after freeze thawing.
In the embodiment, after demulsification and separation by a freeze-thaw method, the separated oil phase passes through an oil purification system (namely an oil purification system), so that oil components can be recycled, the heat value of the recycled oil is close to that of crude oil and is close to average low-temperature heat productivity, the combustion heat value of the recycled oil can reach 37560-39785 kJ/kg, the average low-temperature heat productivity of the crude oil is 41816kJ/kg, and the recycled oil can be used for fuel supply of an incineration system or other ways.
In the water-melting layer of the embodiment, a small amount of oil-in-water emulsification phenomenon exists in a water phase after a water ice crystal layer which is in contact with molten mud and oil is thawed, the water phase contains solid suspended matters, silt, inorganic acid, soluble organic matters, high molecular substances and the like, the COD is about 400-500 ppm, the deep treatment mode adopted by the molten water is flocculation and electron beam irradiation technology treatment, the COD can be treated to below 50ppm, and the wastewater can be directly treated to a direct discharge state; the operation is simple, the electron beam irradiation occupies small area, and the flexibility is high.
The water sample of the water-melting layer after advanced treatment can be discharged up to the standard or recycled to a freeze-thaw system for recycling as dilution water, and the flocculated solid can be incinerated or disposed of.
Wherein, the conditions of electron beam irradiation are as follows: the energy of the electron beam is 1.0-2.5 MeV, and the current is 1-10 mA, which can be continuously controlled. More preferably, the energy of the electron beam is 1.2-1.5 MeV, the current is 1.2-1.5 mA, and the irradiation time is 60-120 s. The accelerated electron beam is used for bombarding the wastewater sample, so that physicochemical and biological reactions which are difficult to initiate by the conventional method occur, and the reaction is completed instantly.
Compared with other treatment methods, the freeze-thaw method adopted by the embodiment has the important characteristic that the treatment energy consumption is lower. Part of the refrigeration energy of the freeze-thaw method can be provided by natural cold energy in nature. The natural cooling energy refers to "low temperature difference and low temperature heat energy naturally existing in a normal temperature environment", and refers to energy obtained by utilizing a temperature difference under a natural condition.
The integrated treatment process of the oily sludge can be optimally selected to be implemented in an extremely cold place, and aims to combine natural cold energy with artificial energy, so that the supply of external artificial energy consumption is reduced, the energy is saved, and the treatment cost is reduced. The average temperature in winter reaches about-20 ℃ in three months in the north every year, particularly in the northeast of Liaohe oil field, and the process is suitable for the process; meanwhile, the burned tailing cooling heat source and the burned tail gas cooling heat source can be recycled through heat exchange and are used for unfreezing a frozen and thawed sludge layer, and the recovered oil can be used as a burning heat source; the wastewater treatment system can quickly treat wastewater to a direct discharge standard, and simultaneously, the wastewater treatment cost is low; the process has strong operability.
Example 2:
the integrated treatment process of the oily sludge of the present example is different from that of example 1 in that:
the number of times of repeated freezing and thawing is not limited to the secondary freezing and thawing described in example 1, and can be adjusted according to the physicochemical properties of the actual oily sludge, and the melted sludge after the primary freezing and thawing is watered for secondary freezing and thawing, so that the oil content of the melted sludge is further reduced until the application requirements are met.
Other steps can be referred to example 1.
The foregoing has outlined rather broadly the preferred embodiments and principles of the present invention and it will be appreciated that those skilled in the art may devise variations of the present invention that are within the spirit and scope of the appended claims.

Claims (10)

1. An integrated treatment process of oily sludge, which is characterized by comprising the following steps:
s1, crushing and homogenizing the oily sludge, and then adding water to control the water content of the sludge to form sludge to be frozen and thawed;
s2, repeatedly freezing and thawing the sludge to be frozen and thawed, wherein three-phase separation is realized by layering of each freezing and thawing, the layered sludge enters next freezing and thawing, and a sludge melting layer, a water melting layer and an oil phase are obtained after the repeated freezing and thawing is completed;
and S3, treating the molten mud in an incineration system, treating the molten water layer in a water treatment system, and treating the oil phase in an oil purification system.
2. The integrated treatment process for oil-containing sludge according to claim 1, wherein in the step S1, the water content of the sludge is controlled to be 60-80%.
3. The integrated treatment process of oily sludge according to claim 2, wherein the water content of the sludge is controlled to be 68-72%.
4. The integrated oily sludge treatment process according to claim 1, wherein the repeated freezing and thawing comprises secondary freezing and thawing, and the melted sludge after the primary freezing and thawing is watered for secondary freezing and thawing.
5. The integrated oily sludge treatment process according to claim 4, wherein the freeze-thaw process conditions comprise: the freezing temperature is-25 to-5 ℃, and the freezing-thawing time is 4 to 15 hours.
6. The integrated oily sludge treatment process according to claim 5, wherein the freeze-thaw process conditions comprise: the freezing temperature is-20 to-15 ℃, and the freezing-thawing time is 8 to 10 hours.
7. The integrated treatment process of oily sludge according to claim 1, wherein the water-melting layer is treated by flocculation and electron beam irradiation in a water treatment system, the treated water is discharged after reaching standards or recycled to freeze-thaw treatment as water supply, and the solid obtained by flocculation is treated in an incineration system.
8. The integrated treatment process of oily sludge according to claim 7, wherein the process parameters of the electron beam irradiation comprise: the energy is 1.2-2.5 MeV, the current is 1-10 mA, and the irradiation time is 60-120 s.
9. The integrated treatment process of oily sludge according to claim 1, wherein the oil phase enters an oil product purification system for treatment to obtain purified oil, and the combustion heat value of the purified oil can reach 37560-39785 kJ/kg.
10. The integrated treatment process of oily sludge according to claim 9, wherein the purified oil is used for supplying energy to an incineration system, and the waste heat of the incineration system is used for defrosting and preheating of the frozen and melted mud and melted water layer.
CN202010564569.6A 2020-06-19 2020-06-19 Integrated treatment process for oily sludge Pending CN111747623A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010564569.6A CN111747623A (en) 2020-06-19 2020-06-19 Integrated treatment process for oily sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010564569.6A CN111747623A (en) 2020-06-19 2020-06-19 Integrated treatment process for oily sludge

Publications (1)

Publication Number Publication Date
CN111747623A true CN111747623A (en) 2020-10-09

Family

ID=72674784

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010564569.6A Pending CN111747623A (en) 2020-06-19 2020-06-19 Integrated treatment process for oily sludge

Country Status (1)

Country Link
CN (1) CN111747623A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113587114A (en) * 2021-07-30 2021-11-02 北京工商大学 High-water-content oil sludge clean combustion treatment device
CN113680106A (en) * 2021-10-25 2021-11-23 山东海吉雅环保设备有限公司 Electron beam irradiation treatment process for aging oil

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1365864A (en) * 1970-10-12 1974-09-04 Hydro Chem & Mineral Corp Treatment of sludge
JPS5286257A (en) * 1976-01-12 1977-07-18 Mitsubishi Electric Corp Organic sludge treating method
JP2000061450A (en) * 1998-08-19 2000-02-29 Matsushita Electric Ind Co Ltd Waste water treatment device and waste water treatment
CN103043838A (en) * 2012-12-26 2013-04-17 大连春兴科技股份有限公司 Freezing and thawing treatment method for suspended wastewater
CN104140188A (en) * 2014-08-04 2014-11-12 饶宾期 Energy-saving type sewage sludge harmless treatment method
CN107879572A (en) * 2017-11-24 2018-04-06 东隆环保科技有限公司 A kind of processing method of oily sludge

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1365864A (en) * 1970-10-12 1974-09-04 Hydro Chem & Mineral Corp Treatment of sludge
JPS5286257A (en) * 1976-01-12 1977-07-18 Mitsubishi Electric Corp Organic sludge treating method
JP2000061450A (en) * 1998-08-19 2000-02-29 Matsushita Electric Ind Co Ltd Waste water treatment device and waste water treatment
CN103043838A (en) * 2012-12-26 2013-04-17 大连春兴科技股份有限公司 Freezing and thawing treatment method for suspended wastewater
CN104140188A (en) * 2014-08-04 2014-11-12 饶宾期 Energy-saving type sewage sludge harmless treatment method
CN107879572A (en) * 2017-11-24 2018-04-06 东隆环保科技有限公司 A kind of processing method of oily sludge

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
GUANGJI HU等: "A combination of solvent extraction and freeze thaw for oil recovery from petroleum refinery wastewater treatment pond sludge", 《JOURNAL OF HAZARDOUS MATERIALS》 *
罗顺忠等: "《核技术应用》", 31 October 2009, 第252-253页 *
陈坤柏等: "《污泥处理与处置》", 31 July 2017 *
陈思等: "含油污泥资源化处理新技术研究现状与展望", 《应用化工》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113587114A (en) * 2021-07-30 2021-11-02 北京工商大学 High-water-content oil sludge clean combustion treatment device
CN113680106A (en) * 2021-10-25 2021-11-23 山东海吉雅环保设备有限公司 Electron beam irradiation treatment process for aging oil

Similar Documents

Publication Publication Date Title
CN107879572B (en) Treatment method of oily sludge
CN102452776B (en) Method for treating oil sludge
CN103739175A (en) Method for processing oil sludge
CN111747623A (en) Integrated treatment process for oily sludge
CN103539325B (en) Process for treating oil-containing sludge and system
CN105731706A (en) Treatment method and device for extremely-high-concentration waste emulsion
CN109970295B (en) Dirty oil sludge treatment equipment and process
JP2001523557A (en) Treatment of refinery effluent
CN111960625A (en) Oil sludge demulsifier and preparation method thereof
CN106830605B (en) Sludge combined treatment method and device
CN108246774B (en) Organic pollutant environment-friendly pyrolysis treatment system and method
CN110407423B (en) Resource recovery processing device for oily sludge
CN103626367A (en) Method for recycling polymer-containing air flotation oil sludge
KR101698575B1 (en) Apparatus and method for purify soil polluted crude
CN103131462A (en) Method for demulsifying crude oil produced liquid through using SD-3 demulsifier
CN110590088A (en) Skid-mounted oil-containing sludge continuous treatment system and treatment method
Golubev et al. Application of magnetic units for intensification of water treatment
CN110407422B (en) Resource treatment method of petrochemical oil sludge
CN210340641U (en) Dirty oil sludge treatment facility
CN110981156B (en) Oil sludge three-phase separation method based on alkali modification
CN208234730U (en) A kind of novel greasy filth Separation process arrangements
KR102018905B1 (en) Multi layer separating bioreactor and method for treatment sludge of sewage using alkane solvent using the same
CN112723698A (en) Harmless treatment system and treatment process for tank cleaning oil sludge
KR20170046501A (en) Apparatus for purify soil polluted crude using activator and air
RU2678589C1 (en) Method of complex processing of an intermediate layer stabilized by iron sulfide

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20201009